DNQ3型能见度仪故障分析及校准方法研究

为有效提高国家地面气象观测站能见度仪观测数据准确性和设备运行稳定性,对能见度仪开展日常维护、核查校准、数据质控和故障修复等工作显得尤为重要。该文通过对DNQ3型前向散射能见度仪硬件结构和基本工作原理的介绍,以及对一些典型故障进行分析,总结出能见度仪的检测维修流程,归纳了对应的故障解决措施,凝练出该型能见度仪的核查校准和疑误数据质控方法,为一线业务人员开展能见度仪常规维护、故障排查、运行监控等提供借鉴。     

河北省丰宁县茶棚银矿地质、地球物理特征及找矿意义

茶棚银矿位于河北省北部坝上草原向山区过渡地带,风成砂覆盖严重,示矿标志不明显,地表找矿难度大;地表矿体断续出露,而深部银矿体主要以隐伏矿体的形式赋存于近南北向展布的构造破碎带中,数量明显增多、品位变富、厚度变大;在这种特殊的景观地质特征下,利用激电中梯扫面,可发现厚覆盖状态下构造矿化蚀变带,利用EH4连续导电率测量可厘定矿化蚀变带的规模、产状并可提供隐爆角砾岩体等深部控矿地质信息,利用可控源音频大地电磁测深的中低阻陡变带和中阻带,特别是陡变带中的转折部位（形态呈耳状部位）可具体定位银矿体的赋存空间。     

线路圆曲线的解算方法探讨

探讨一种数值求解圆曲线基本元素的通用方法。采用这一方法能以给定的任意两个基本元素,解算出圆曲线半径和两切线方向间的偏角。该方法计算简便、快捷,有较大的实用价值。     

洞庭湖区域黑线姬鼠（Apodemus agrarius）种群迁入湖滩后的繁殖特征

黑线姬鼠(Apodemus agrarius)是广泛分布于我国的主要农田害鼠之一,2003年三峡工程开始蓄水后洞庭湖湖滩鼠类群落结构发生了演变,黑线姬鼠已大量侵入湖滩,且逐步成为湖滩生境鼠类群落的优势鼠种。动物在新生境中的繁殖状况是了解其对环境适应的关键指标。为掌握黑线姬鼠种群侵入湖滩生境后的适应情况,为其种群动态的预测预报提供科学依据,本文对2003—2020年洞庭湖湖滩和农田生境中捕获的黑线姬鼠繁殖状况进行比较分析,并结合季节动态和生境差异等因子分析了该鼠在繁殖方面对湖滩生境的适应。结果表明:(1)湖滩生境中黑线姬鼠平均繁殖指数(0.71±0.27)低于农田生境(1.21±0.47),在2016—2020年湖滩上黑线姬鼠的繁殖指数为0.99,略高于农田的0.96;(2)湖滩生境较农田生境中的孕鼠在繁殖中偏向有更多的胎仔数,有6只以上胎仔数的孕鼠占比(65.59%)高于农田生境(49.10%);(3)湖滩生境中发现有幼年组的黑线姬鼠参与繁殖,其繁殖指数、参产率、怀孕率及雄鼠的睾丸下降率随年龄递增;(4)春季和秋季是湖滩生境中黑线姬鼠的主要繁殖季节,其繁殖指数、参产率、怀孕率都显著高于...     

桂林暴雨天气的多普勒雷达径向速度分析与应用

利用桂林新一带天气雷达径向速度产品资料对2004年发生在桂林的强暴雨过程及其暴雨个例的径向速度平面位置显示产品（PPI）特征的多样性进行分析发现，利用径向速度变化可判断中尺度对流的发展，可对桂林暴雨提前做出预报。     

东营凹陷民丰地区深部储层成岩环境变化研究

通过薄片鉴定、激光拉曼光谱分析、全岩和粘土矿物分析以及流体包裹体测试等手段,结合埋藏史分析,研究了东营凹陷民丰地区深部储层成岩环境的特点。分析认为,东营凹陷民丰地区深部储层成岩现象丰富,表现出不同成岩环境相叠合的特征,存在酸性、碱性和酸性碱性交替等多重成岩环境。着重利用不同成岩环境代表矿物中的流体包裹体分析成岩环境的变化,结果显示,3 000~3 200 m是碱性流体活动的重要深度。东营凹陷民丰地区深部储层在埋深过程中由浅到深大致经历了（弱）碱性（小于1 750 m）→酸性（1 750~3 200 m）→酸碱交替（3 200~4 000 m）→碱性（4 000~5 000 m）→弱碱性到弱酸性（大于5 000 m）多重成岩环境的变化,从而形成了现今复杂的成岩现象。埋深和温度是成岩环境变化的宏观主导因素,但并非绝对控制因素,局部流体性质的变化更能直接导致成岩环境的变化。     

Quantification of electrical resistance to estimate NaCl behavior in a column under controlled conditions

Accurate prediction of solute transport processes in surface water and its underlying bed is an important task not only for proper management of the surface water but also for pollution control in these water bodies. Key issue in this task is an estimation of parameters as diffusion coefficient and velocity for solute transport both in water body and in the underlying bed. This estimation would greatly help us to understand the deposition and release mechanism of solute across the water-bed interface. In this study, a column experiment was conducted in laboratory to estimate the velocity and diffusion coefficient of sodium chloride (NaCl) in water body and underlying sand layer (bed). The column used with a diameter of 30 cm and a height of 100 cm, was filled with sand at the lower half part and water at the upper half part. Total 64 stainless steel electrodes were installed on its surface around. The sodium chloride solution was injected from the top of the column, and electrical resistance between electrodes was monitored for 71 h. Then the dimensionless resistance breakthrough curve was fitted with one dimensional analytic solution for solute transport and the related diffusion coefficient and velocity parameters were estimated. The results show that the NaCl transport velocity was high in the water body but extremely low in the underlying sand layer (bed). The diffusion coefficient estimated in sand layer coincides with those reported well. This indicates that the electrical resistance based solute transport parameter estimation method is not only effective but also has an advantage of multipoints monitoring. This is useful both in mapping solute transport parameter for solute transport process analysis and in providing parameter input for solute transport numerical modeling.     

近40年天山冰川变化的遥感监测

Both marginal fluctuation and areal change were used to detect the accurate dynamics of glacier change in the study area using Landsat MSS, ETM, SPOT HRV and topographic maps based on GIS. From 1963 to 1977, four of eight glaciers advanced, two of them retreated and another two kept stable, the glacier advanced generally. From 1977 to 1986, four of eight glaciers retreated and the others kept stable, but the retreated glaciers were those which advanced from 1963 to 1977. From 1986 to 2000, seven of eight glaciers retreated and only one glacier kept stable, the retreating velocity was 10-15 m/a. Glacier recession in this period became very fast and universal. From 1963 to 2000, the area of glaciers decreased from 5479.0 ha to 4795.4 ha, up to 12.5%. It is alarming that most of glacier retreats happened from 1986 to 2000. This was very consistent with change process of summer mean temperature in this region and global warming beginning in the 1980s.     

Evolution of the freeze-thaw cycles in the source region of the Yellow River under the influence of climate change and its hydrological effects

As an important water source and ecological barrier in the Yellow River Basin, the source region of the Yellow River (above the Huangheyan Hydrologic Station) presents a remarkable permafrost degradation trend due to climate change. Therefore, scientific understanding the effects of permafrost degradation on runoff variations is of great significance for the water resource and ecological protection in the Yellow River Basin. In this paper, we studied the mechanism and extent of the effect of degrading permafrost on surface flow in the source region of the Yellow River based on the monitoring data of temperature and moisture content of permafrost in 2013–2019 and the runoff data in 1960–2019. The following results have been found. From 2013 to 2019, the geotemperature of the monitoring sections at depths of 0–2.4 m increased by 0.16°C/a on average. With an increase in the thawing depth of the permafrost, the underground water storage space also increased, and the depth of water level above the frozen layer at the monitoring points decreased from above 1.2 m to 1.2–2 m. 64.7% of the average multiyear groundwater was recharged by runoff, in which meltwater from the permafrost accounted for 10.3%. Compared to 1960-1965, the runoff depth in the surface thawing period (from May to October) and the freezing period (from November to April) decreased by 1.5 mm and 1.2 mm, respectively during 1992–1997, accounting for 4.2% and 3.4% of the average annual runoff depth, respectively. Most specifically, the decrease in the runoff depth was primarily reflected in the decreased runoff from August to December. The permafrost degradation affects the runoff within a year by changing the runoff generation, concentration characteristics and the melt water quantity from permafrost, decreasing the runoff at the later stage of the permafrost thawing. However, the permafrost degradation has limited impacts on annual runoff and does not dominate the runoff changes in the source region of the Yellow River in the longterm.